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    Opportunit ies for Efficiency Improvements inPower Plants with Carbon Capture

    Author:

    Suzanne Ferguson

    Foster Wheeler Energy Limited

    Co-authors:

    Tim BullenGeoff Skinner

    Foster Wheeler Energy Limited

    Presented at

    Power-Gen Europe 2010

    Rai, Amsterdam

    The Netherlands

    June 8 10, 2010

    TP_CCS_10_04

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    Abstract

    The current technologies for CO2 capture from power generation processes result in significant plant

    efficiency penalties. This paper identifies the main efficiency penalties and explores potential

    technology solutions to improve the overall plant efficiency of plants which include carbon capture.

    A number of large-scale power generation schemes will be considered, including pulverised coal,

    natural gas combined cycle, and integrated gasification combined cycle (IGCC) schemes. The carbon

    capture schemes considered will include a number of available technologies for both pre- and post-

    combustion capture, considering the implications for both new-build and retrofit projects. The paper

    will explore areas where there is potential for significant reductions in either parasitic load or improved

    efficiency of key unit operations, reduction in steam demand and/or increased capture efficiency.

    It can be seen that in a few specific areas of each power generation flow scheme, there are significant

    efficiency improvements which can be achieved. While some of these are emerging technologies,

    which require further development and demonstration, and may be five or more years in the future,

    others can be achieved simply through improved process and heat integration and could be realised

    immediately. Many of these possible improvements have not been fully explored during carbon

    capture literature paper studies or in the operation of pilot plants.

    Introduction

    Climate change resulting from increased levels of atmospheric greenhouse gases such as carbon

    dioxide (CO2) could, many believe, be a serious threat to the environment and the world economy. A

    significant portion of these CO2emissions are emitted into the atmosphere when hydrocarbon fuels are

    burned to produce energy, particularly in the power sector. One emerging technology, or set of

    technologies, that has been proposed to mitigate future CO2emissions is carbon capture and storage

    (CCS).

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    Carbon capture can be applied to oil-, coal- or natural gas-based electricity generation, and there are

    three process routes that can be considered. These are:

    pre-combustion capture

    post-combustion capture

    oxyfuel combustion.

    This paper aims to identify areas in which significant improvements to the efficiency of carbon capture

    power generation schemes may be anticipated and to quantify the impact on the overall efficiency of a

    plant with carbon capture.

    The power generation systems considered within the scope of this paper are an ultra-supercritical

    pulverised coal-fired steam cycle, a natural gas combined cycle and an integrated gasification

    combined cycle. Oxyfuel combustion has also been studied by Foster Wheeler, however, it has not

    been included in this paper in order to limit it to a reasonable scope. The baseline configurations for

    each type of plant are outlined below:

    Ultra-Supercritical Pulverised Coal

    (USCPC)

    Figure 1: Pulverised Coal Simplified Flowscheme

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    For this case a single pulverised coal-fired unit of nominally 800 MWe capacity was assumed. The

    boiler was simulated as raising steam at 275 bara/600C with single reheat to 600C, and incorporating

    selective catalytic reduction (SCR) for nitrous oxides (NOx) removal, an electrostatic precipitator

    (ESP) for particulate removal and limestone scrubbing for sulphur dioxide (SO2) removal. An amine-

    based post-combustion carbon capture process was applied to this plant, followed by CO2compression

    to 150 barg with CO2dehydration.

    Natural Gas Combined Cycle Gas Turbine (CCGT)

    Figure 2: Natural Gas Combined Cycle Simplified Flowscheme

    A modern arrangement of two G-class gas turbines and a single steam turbine producing approximately

    1,000 MWe was used for the combined cycle gas turbine case (CCGT) with CO 2capture. Each gas

    turbine is fitted with its own heat recovery steam generator (HRSG) feeding the single steam turbine.

    An amine-based post combustion carbon capture process was applied to this plant followed by CO2

    compression to 150 barg with CO2dehydration, very similar to that applied to the pulverised coal plant.

    Integrated Gasification Combined Cycle

    (IGCC)

    Figure 3: Integrated Gasification Combined Cycle Simplified Flowscheme

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    The IGCC plant comprises two gasification lines supplied by a common air separation unit (ASU), two

    F-class gas turbines with heat recovery steam generators (HRSGs) and a common steam turbine. The

    conventional air separation unit (ASU) supplies oxygen to the gasifiers and sulphur recovery unit and

    also supplies nitrogen for coal conveying and for dilution of hydrogen-rich gas turbine fuel gas.

    In each gasification line coal is milled and dried and fed to an entrained-flow gasifier. The product gas

    flows through heat recovery with steam generation, particulate removal filtration, sour shift (which also

    performs COS hydrolysis) and syngas cooling with heat recovery. A selective DEPG (polyethylene

    glycol dimethyl ether) unit first removes hydrogen sulphide (H2S) and then CO2. The H2S rich stream

    is treated in a Claus sulphur removal unit (SRU) and tail gas treating unit (TGTU), while the CO2rich

    stream is compressed to 150 barg and dehydrated for export to storage. The hydrogen-rich stream isdiluted with nitrogen before combustion in the gas turbines.

    Parasitic Loads due to addition of Carbon Capture

    When carbon capture is applied to power generation it reduces the overall efficiency of the plant by

    introducing a number of parasitic loads resulting in more energy being used internally to the power

    plant leaving less available for export. These parasitic loads can be caused either by electrical loads

    such as additional rotating machinery or as thermal loads such as the heat required for regenerating

    solvents. The heat requirement reduces the power produced since steam which would have been used

    for generating electrical power has instead been used as a heat source.

    In order to improve the overall efficiency of a power plant with carbon capture it is necessary to reduce

    or eliminate as much energy demand as possible whether it is thermal or electrical. Improving theperformance of a solvent by additional cooling, hence requiring less heat for regeneration, is not always

    a solution if it requires a significant increase in electrical load due to the requirement for chilling or

    refrigeration systems. It is therefore necessary to consider the power plant system as a whole in order

    to identify sensible targets for savings that can be made.

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    Ultra-Supercritical Pulverised Coal (USCPC)

    Figure 4: Pulverised Coal Key Parasitic Loads

    Applying a monoethanolamine (MEA)-based post-combustion unit (currently the most demonstrated

    type of technology for post-combustion carbon capture) to the pulverised coal plant introduces two

    main parasitic loads and a number of lesser loads. Firstly a significant quantity of low pressure steam

    is required for solvent regeneration, reducing the electrical output of the steam turbine generator. The

    second load is the power needed to drive the CO2compressor.

    Of the lesser loads, the largest is often the flue gas blower required to elevate the pressure of the entire

    flue gas stream sufficiently to overcome the pressure drop across the absorption column and anyassociated heat exchangers. Other lesser loads include pumping power and or fan power associated

    with a significant quantity of cooling medium and transport of the solvent around the capture plant

    loop. Based on previous work by Foster Wheeler the typical loads are as follows;

    Load added to apply CO2Capture % of total additional load

    Solvent Reboiler 56 %

    CO2Compression 33 %

    Flue Gas Blowers 4 %

    Others 7 %

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    Table 1:Pulverised Coal Parasitic Load Breakdown

    Solvent regeneration reboiler This duty has been extensively targeted for reduction by improving or

    changing solvents, or by flashing a portion of the lean solvent to generate a semi-lean stream(1)

    . Study

    work undertaken by the International Energy Agency Greenhouse Gas Research & Development (IEAGHG R&D) Programme estimates that savings of from 27 to 40% on regeneration energy requirement

    can be made compared to conventional processes(5)

    . A saving of 30% on reboiler duty will be

    considered for the purposes of this paper.

    CO2compressor power Recently much work has also been done to investigate means of reducing

    the power requirement for CO2 compression. In a recent paper by GE(2)

    savings of up to 20% are

    anticipated by varying the compression route and achieving liquefaction at the lowest possible pressure

    for the available cooling medium. Further savings could be achieved by introducing refrigeration

    cycles, however, the power requirement of the refrigeration cycle was shown to offset the benefit of

    increased CO2 compression chain efficiency. A saving of 20% on CO2 compressor power will be

    considered for the purposes of this paper, in line with GEs findings(2)

    .

    Integration There is a significant requirement for cooling in the amine-based post-combustion

    carbon capture flow scheme which results in low grade waste heat which may be recovered elsewhere

    on the plant. It has been shown that, depending on the individual site circumstances (such as available

    cooling medium temperature), a greater degree of compressor intercooling can be preferable in overall

    plant efficiency terms to recovery of CO2compressor waste heat. There is, however, still a significant

    quantity of recoverable waste heat available from the stripper condenser and solvent coolers to

    integrate with the power island boiler feed water preheating. This integration reduces the quantity of

    steam which is extracted from the steam turbine to preheat the boiler feed water, hence increasing the

    electrical output of the steam turbine generator. A saving of one percentage point on overall powerplant efficiency will be considered for the purposes of this paper based upon the results of previous

    Foster Wheeler study work integrating carbon capture with this type of plant.

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    Incorporating each of the suggested improvements above into our base case flowscheme for the

    pulverised coal plant results in an increase in the net power output of approximately 9% and

    consequently an increase of approximately three percentage points in overall efficiency.

    Natural Gas Combined Cycle Gas Turbine (CCGT)

    Figure 5: Natural Gas Key Parasitic Loads

    The natural gas flowsheme with post-combustion carbon capture is characterised by similar parasitic

    loads as for the pulverised coal case above. The main difference is the proportion of these loads. Since

    the flue gas from a combustion turbine is significantly more dilute, the blower power is proportionately

    higher, and hence is a more significant parasitic load on the plant. In general however, other parasiticloads, all those associated with the total mass of CO2 to be captured, are lower due to the smaller

    quantity of CO2generated by combustion of natural gas compared with combustion of coal. Based on

    previous work by Foster Wheeler the typical parasitic loads are as follows,

    Load added to apply CO2Capture % of total additional load

    Solvent Reboiler 54 %

    CO2Compression 20 %

    Flue Gas Blowers 19 %

    Others 7 %

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    Table 2:Natural Gas Parasitic Load Breakdown

    Solvent regeneration reboiler&CO2compressor power Since the post-combustion flowscheme is

    almost identical for a natural gas plant as for a pulverised coal plant the same improvements can be

    assumed for the reboiler duty (30% reduction in thermal energy) and the CO2compression power (20%reduction in electrical power) as for the pulverised coal case.

    Flue Gas Blower Less industry work has focused on investigating potential reductions in the flue gas

    blower power. The blower is required to overcome the pressure drop incurred through the CO2

    absorber and any heat exchangers and ducting between the power island and the carbon capture plant.

    While one option would be to consider future improvements in blower efficiency, an alternative

    solution would be to give high priority to minimising pressure drop between the power island and the

    capture plant. This could be achieved by minimising the physical distance between the two and

    modifying design of the heat exchangers and pipework to minimise losses. An assumed saving of 10%

    on blower power due to reduced system pressure losses will be considered for the purposes of this

    paper in order to assess the impact such a saving would have on the overall plant efficiency.

    Gas Turbine Improvements The design of gas turbines is under constant scrutiny to find areas for

    improvements in efficiency. Since the gas turbines produce approximately two-thirds of the total

    combined cycle power any small improvement in efficiency results directly in a proportionate

    improvement in the plant overall efficiency. Gas turbines are improved both by the introduction of

    new models and by modifications to existing designs. Gas Turbine World publishes historic

    information on improvements made to currently available gas turbine designs varying from 0% to 7%

    depending on the type of machine(4)

    . Using this data as a basis to extrapolate future GT improvements

    an increase of 3% in GT efficiency will be considered for the purposes of this paper.

    Integration Recovery of carbon capture plant waste heat is more challenging in the natural gas

    combined cycle case due to the high level of thermal integration already applied within the power

    island(3)

    . Boiler feed water preheating is already achieved within the coolest section of the HRSG,

    hence more complex integration studies would be required on a project-specific basis if further heat

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    integration savings were to be identified. Solutions such as optimisation of steam generation pressure

    levels, integrating boiler feed water preheating with the capture plant direct contact cooler, preheating

    rich solvent upstream of the stripper and reboiling a portion of the stripper bottoms in the HRSG might

    be considered. This degree of integration should be performed in conjunction with capital and

    operating cost estimation in order to determine the appropriate degree of integration without excessive

    additional investment cost. This has not been undertaken for this paper. Hence no efficiency

    improvement due to additional heat integration has been assumed for the natural gas case.

    Incorporating each of the suggested improvements above into the our base case flowscheme for the

    natural gas combined cycle plant results in an increase in the net power output of approximately 7%

    and consequently an increase of approximately three percentage points in overall efficiency.

    Integrated Gasification Combined Cycle (IGCC)

    Figure 6: IGCC Key Parasitic Loads

    The integrated gasification combined cycle scheme consists of a more complex process scheme than

    the post-combustion capture cases, with more process units requiring either heat or power or both. The

    main power users are the air separation unit (ASU), CO2 compression and acid gas removal unit

    (AGR), while the main users of steam are the AGR and the Shift.

    Based on previous work by Foster Wheeler the following table summarises the distribution of the

    additional parasitic loads of an IGCC power plant due to adding carbon capture:

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    Load added to apply CO2Capture % of total additional load

    DEPG-based CO2Removal 46 %

    CO2Compression 26 %

    Others 28 %

    Table 3:IGCC Parasitic Load Breakdown Due to Addition of CO2Capture

    Table 3 above shows the very significant contribution to the parasitic loads resulting from the use of

    steam in the AGR. However, when all of the parasitic power loads (excluding heat loads) on the plant,

    not just those due to adding carbon capture, are compared the picture looks somewhat different:

    Parasitic Power Load % of total power load

    DEPG-based CO2Removal 14 %

    Air Separation Unit 47 %

    CO2Compression 21 %

    Others 18 %

    Table 4:Overall IGCC Plant with CO2Capture Parasitic Load Breakdown

    Table 4 shows that nearly half of all power which is consumed within the power plant is due to the

    ASU, which only increases in duty by a relatively small amount when adding carbon capture to the

    IGCC scheme.

    The contribution of others to the plant parasitic loads is also significant. Improving the efficiency of

    heat recovery from gasification, energy conversion in the gasifiers and operation of the gas turbines

    also present opportunities for improving the efficiency of the overall IGCC plant with carbon capture.

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    Gasification Improvements -

    Entrained flow gasifiers can be provided with mechanical coal pumping, avoiding need for

    high pressure coal conveying nitrogen.

    Medium temperature gasification with outlet gas around 1000C reduces oxygen

    consumption, reduces cost of heat recovery and increases the gas turbine contribution to total power

    output. Medium temperature gasifiers include two-stage entrained flow, fluidised bed and transport

    gasifier types.

    Fixed bed gasification with outlet gas around 500C further reduces oxidant consumption

    and may be an attractive but so far little explored option.

    Medium- and low-temperature gasification open the way to practical use of air or enriched

    air in place of oxygen.

    Based on these factors it is anticipated that an overall efficiency improvement of 0.5 percentage points

    could be realised due to gasification improvements and hence 0.5 percentage points improvement has

    been assumed for this paper.

    Gas Turbine - One factor, not often recognised, limiting the thermal efficiency of IGCC with carbon

    capture is the generally low firing temperature of gas turbines fuelled with decarbonised fuel (basically

    hydrogen with nitrogen or steam dilution). The installed GT exhaust temperature of F-class GTs firing

    natural gas is around 600C Gas Turbine World quotes 602C for the GE 9FA in open cycle and

    638C for the 9FB in combined cycle[4]

    - while representative exhaust temperatures recommended by

    manufacturers for firing of decarbonised fuel gas are of the order of 50C to 80C lower. Several

    factors are seen as contributing to this downrating:

    Potential hot component corrosion by higher steam content from combustion of H2-rich fuel

    Lower calorific value of the decarbonised fuel increases exhaust flow rate, increasing

    mechanical stresses this can be alleviated by air extraction

    Perceived need to meet NOXemission limits with existing diffusion burners without resort

    to SCR

    Understandable conservatism in absence of significant operating experience.

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    A simulation performed by Foster Wheeler has shown the potential for increasing the thermal

    efficiency of an IGCC plant with carbon capture by approximately four percentage points just through

    increasing the GT exhaust temperature to 626oC. This represents the best single potential improvement

    in gasification-based power with carbon capture, far more significant than any improvement in the

    syngas production process.

    Other potential GT improvements include:

    higher GT fuel gas preheat

    lower burner pressure drop, reducing the fuel gas pressure upstream of the GT and hence

    reducing the resulting oxygen and diluent nitrogen supply pressures requirements

    improved burners and other hot components, permitting high firing temperatures and/or lessdilution of the decarbonised fuel gas with nitrogen or steam

    premix burners for use with higher firing temperatures, as alternative to SCR for NOx

    emission control

    reduced capacity GT air compressor, as substitute for air extraction

    An overall efficiency improvement of four percentage points has been applied for this paper due to GT

    performance improvements, mainly due to increased exhaust temperature.

    Air separation unit - Large oxygen production plants currently use cryogenic air distillation, which

    has been practiced for more than 100 years. Cryogenic oxygen production is a highly energy intensive

    process, with typical power consumption for 95% purity oxygen of approximately 320 to 350 kWh /

    tonne O2 delivered at gasifier pressure using current technology. Large quantities of oxygen are

    required by IGCC and oxyfuel power generation, for example, approximately 4,700 tonnes/day for a

    700MWnet IGCC plant with carbon capture. Oxygen production plants also account for a significant

    portion of the capital cost of IGCC with carbon capture plants - approximately 10%. The significant

    contributors to the inefficiency of the air separation process are the air compression, the process

    pressure drops (notably heat exchangers and distillation columns) and heat exchanger temperature

    differences. Improvements in one or more of these increases in air compression efficiency and the use

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    of more complex and integrated air separation unit process cycles have the potential to reduce the

    energy consumption of cryogenic air separation.

    Alternatively, Ion Transport Membranes (ITM) or Oxygen Transport Membranes (OTM) technologies

    are currently being developed. ITMs use dense mixed metallic oxides which are oxygen selective. They

    operate at between 800 900C producing a high purity oxygen permeate stream and a nitrogen rich

    non-permeate stream suitable for syngas fuel dilution. Studies indicate that ITMs could significantly

    reduce the net capital and power costs for oxygen production by around 35%. However, ITMs have not

    been demonstrated in large scale plants, so their savings are not yet proven[6]

    .

    Work undertaken by others indicates that an overall efficiency improvement of approximately 1.2

    percentage points is achievable through the use of ITM compared with a cryogenic ASU[6]

    , therefore

    1.2 percentage points improvement has been assumed for this paper.

    CO2compressor power Similarly to the USCPC and CCGT cases much recent work has been done

    to investigate possible means of reducing the power requirement for CO2compression. Similar levels

    of power and efficiency savings as in the USCPC and CCGT cases would be anticipated for the IGCC

    case. A saving of 20% on CO2compression power will be considered for the purposes of this paper.

    Incorporating all of the suggested improvements above into the our base case flowscheme for the

    integrated gasification combined cycle plant results in an increase in the net power output of

    approximately 17% and consequently an increase of approximately six percentage points in efficiency.

    Shift -Another important point to consider in IGCC schemes is the reduction in efficiency due to the

    water gas shift reaction. Greater conversion of CO to CO2is necessary as the required CO2capture rate

    increases. To achieve this increased quantities of steam are required for the shift reaction. This in turn

    reduces the steam available to the steam turbine and correspondingly the steam turbine electrical

    output, combined with increasing the quantity of make-up water required. Use of a lower CO2capture

    rate would reduce the impact of this aspect of the IGCC process, however this has not been considered

    in this paper.

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    Results

    Three generic power plant configurations with carbon capture have been considered, investigating

    potential for reductions in parasitic power and heat demand and improved integration. The suggested

    improvements were incorporated into a baseline design to quantify the resultant total improvements in

    plant efficiency with carbon capture from the baseline.

    The following table summarises the improvements applied to the baseline flowschemes for this study:

    Case Technology Impact

    Ultra-

    Supercritical

    Pulverised Coal

    (USCPC)

    Capture Plant Regeneration Duty 30% reduction in heat load

    CO2Compressor Power 20% reduction in power load

    Integration1% point increase in overall LHV

    efficiency

    Natural Gas

    Combined

    Cycle Gas

    Turbine

    (CCGT)

    Capture Plant Regeneration Duty 30% reduction in heat load

    CO2Compressor Power 20% reduction in power load

    Blower Duty 10% reduction in power load

    Gas Turbine Efficiency 3% increase in GT efficiency

    Integrated

    Gasification

    Combined

    Cycle (IGCC)

    Gasification Improvements0.5 % point increase in overall

    LHV efficiency

    Gas Turbine Improvements4 % point increase in overall LHV

    efficiency

    CO2Compressor Power 20% reduction in power load

    Air Separation Unit Power

    1.2 % point increase in overall

    LHV efficiency

    The following table summarises the results calculated for this paper, where carbon capture has been

    abbreviated to CC:

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    Penalty due to

    addition of

    conventional CC

    Penalty due to addition

    of CC with suggested

    technological

    improvements

    Benefit due to

    potential

    technological

    improvements

    Case

    Net

    Power

    (%)

    LHV

    Efficiency

    (1)

    Net

    Power

    (%)

    LHV

    Efficiency

    (1)

    Net

    Power

    (%)

    LHV

    Efficiency

    (1)

    Ultra-

    Supercritical

    Pulverised Coal

    (USCPC)

    20.7 8.9 13.4 5.7 7.3 3.2

    Natural Gas

    Combined Cycle

    Gas Turbine

    (CCGT)

    15.4 9.0 9.6 5.7 5.8 3.3

    Integrated

    Gasification

    Combined Cycle

    (IGCC

    20.1 9.0 6.4 2.8 13.7 6.2

    Note 1. Efficiency units are quoted as percentage points.

    Conclusions

    It is clear that carbon capture has a key part to play in decarbonising the power generation sector.

    However, it is widely recognised that current carbon capture technologies and configurations exhibit a

    significant efficiency and electrical output penalty compared with unabated power plant design. This

    paper has identified a number of potential areas of improvement. In all individual plant cases there will

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    be variations in the efficiency improvements that can be realised, depending amongst other things, on

    the baseline design employed and specific basis of design.

    In the USCPC case our study has shown a cumulative efficiency improvement of over three percentage

    points can be made. Considering a current delta of approximately nine percentage points between theefficiency of USCPC schemes with and without carbon capture this represents 35% improvement.

    This compares to the CCGT case for which our study has identified a potential cumulative efficiency

    improvement of over three percentage points. Considering a current delta of approximately nine

    percentage points between the efficiency of CCGT schemes with and without carbon capture this again

    represents almost 40% improvement.

    Most encouraging of the three is the IGCC case. Our study has shown a cumulative efficiency

    improvement of more than six percentage points can be made, dominated by the gas turbine.

    Considering a current delta of approximately nine percentage points between the efficiency of IGCC

    schemes with and without carbon capture this represents almost 70% improvement.

    Further analysis is recommended to understand the capital and operating costs associated with thedesign adjustments necessary to achieve the efficiency improvements reported, thereby enabling the

    economic impact to be understood, in terms of levelised cost of electricity, cost of CO2captured and

    cost of CO2avoided.

    2010 Foster Wheeler. All rights reserved

    References

    1) C.A. Roberts, J. Gibbins, R. Panesar & G.Kelsall, Potential for Improvements in Power

    Generation with Post-Combustion Capture of CO2,

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    2) C. Botero & Co (GE Global Research Centre) & S. Bertolo & Co. (GE Oil & Gas),

    Thermoeconomic Evaluation of CO2Compression Strategies for Post Combustion CO2Capture

    Applications, GE Oil & Gas Technology Insights 2010.

    3) F. Cinelli, A. Miliani & G. Seghi (GE Oil & Gas) & M. Lehar (GE Global Research Centre,

    Reducing the CO2 Footprint Through Increased Overall Cycle Efficiency, GE Oil & Gas

    Technology Insights 2010.

    4) Improved GT Designs (2005 2009), Gas Turbine World 2009 GTW Handbook, Volume 27,

    2009, Pequot Publishing Inc.

    5) IEA Greenhouse Gas R&D Programme (IEA GHG), Evaluation of Novel Post-Combustion

    CO2Capture Solvent Concepts, 2009/14, November 2009.

    6) IEA Greenhouse Gas R&D Programme (IEA GHG), Improved Oxygen Production

    Technologies, 2007/14, October 2007.